Diptera) in Delineating Ecological Classifications of Missouri Streams at Different Environmental Scales

Congruence between nutrient water quality parameters and Chironomidae (Diptera) in delineating ecological classifications of Missouri streams at different environmental scales. Kansas Biological Survey Report No. 159 Dec. 2009 by Barbara Hayford*, Donald Huggins†, Debra Baker†, and Michael Johnson‡ †Central Plains Center for BioAssessment Kansas Biological Survey University of Kansas, Lawrence, KS, U.S.A. *Department of Life Sciences Wayne State College, Wayne, NE, U.S.A. ‡Aquatic Ecosystems Analysis Laboratory John Muir Institute of the Environment University of California, Davis, CA, U.S.A. 1 SUMMARY 1. Large scale classifications such as nutrient ecoregions have been established in the United States to help regulate surface water resources. These classifications and their constituent classes are hypotheses which may be tested by establishing the strength of the classes to differentiate within class and between class variation. The purpose of our study was to test the strength of three different classification schemes at three different scales: landscape (nutrient ecoregion), watershed (hydrologic unit), and microhabitat (substrate) using Chironomidae community assemblage and metric data and nutrient water quality data. Furthermore, we tested for congruence of classes using nutrient water quality and chironomid community data for the three classification schemes in an attempt to link the biota to nutrient concentrations. 2. Historical data on chironomid communities were compiled from the 20 stream sites in Missouri over multiple years and seasons. Nutrient water quality data were also collected at these sites but under a different study. An analysis of variance was used to determine whether chironomid metrics and nutrient water quality parameters varied significantly between classes for each of the classification schemes. Chironomid community assemblages and metrics and nutrient water quality parameters were used to test the strength of each classification. A mantel test for congruence was used to determine how congruent the classes were for each classification scheme based on three data matrices: chironomid community assemblages; chironomid metrics; and nutrient water quality parameters. 3. The three classification schemes were robust enough to show significant variation between nutrient water quality concentrations, chironomid community assemblages, and chironomid metrics. The classifications based on the nutrient data were strong and the classifications based on the chironomid assemblage and metric data were weak, although comparable to classification strengths based on entire macroinvertebrate communities and fish communities for regional, watershed/basin, and substrate classes. 4. Despite relatively weak classification based on chironomid data, all data were able to separate out the different nutrient ecoregions. Variation from classes of watershed and basin that transcended nutrient ecoregions and from substrates at a very fine environmental filter were not strong enough to break up the grouping of nutrient ecoregions, and therefore were not responsible for the relatively weak classification strengths observed. Finally, the chironomid metric and assemblage data were significantly congruent with the nutrient data but were not strongly correlated indicating that nutrient and biological data can be combined under the nutrient ecoregion classification, but with some caution. Keywords: Nutrient ecoregions, classification strength, Chironomidae, mantel test, substrate, hydrologic units 2 Introduction Classifications are useful tools in aquatic ecology and biological assessment because they allow researchers to examine communities of aquatic organisms within naturally occurring regions at varying scales. Regional classification schemes have been useful in delineating communities of fish (Rohm et al., 1987; Whittier et al., 1988; Van Sickle and Hughes, 2000) and macroinvertebrates (Whittier et al., 1988; Rabeni and Doisy, 2000; Sandin and Johnson, 2000; Johnson, 2000; Mykra et al., 2004). However, tests of the strength of a priori classifications such as ecoregions have shown that some classes are weak, particularly between relatively similar ecoregions (Hawkins and Vinson, 2000; Gerritsen et al., 2000), but classes increased in strength when combining similar ecoregions and then comparing them to markedly different ecoregions (Gerritsen et al., 2000). It is likely that some classification schemes will be very useful for water resource managers to identify natural variation between classes; whereas other classifications will be weak due to within class stream heterogeneity (Hawkins and Vinson, 2000; Mykra et al., 2004). Nutrient ecoregions are a regional scale classification for use in managing U.S. surface waters for nutrient criteria (Gibson et al., 2000). Classes of nutrient regions were formed from aggregates of level III ecoregions (Omernik 1987) and were based on natural and anthropogenic features that affect nutrient loads (Gibson et al., 2000). Although formed for use in creating benchmarks for concentrations of total nitrogen, total phosphorus, chlorophyll a and turbidity, they may also prove useful in creating benchmarks for biocriteria; thus, establishing congruence between water quality parameters and community assemblage and biological metric data may provide supporting evidence for a causal link between variation in nutrient criteria and biological communities within the regulatory framework of nutrient ecoregions and nutrient benchmarks. Classifications are based on three hypotheses: one, that the class is a naturally occurring class rather than a convenience class (e.g. Wiley, 1981); two, that researchers accurately delineate the naturally occurring class (Omernik and Bailey, 1997); and three, that environmental filters working at the scale of the classification select for the communities present within the classification (Chessman and Royal, 2004). Environmental filters are factors that determine the distribution and abundance of species and consequently, the composition of biological communities. Environmental filters can be either physical (e.g. substrate) or chemical (e.g. nutrient concentrations). Assuming that the first hypothesis is correct, we can test the second and third hypotheses for nutrient ecoregions by looking for significant variation in Chironomidae (Diptera) and select nutrient water quality constituent values between regions and by testing the strength of the classes of nutrient ecoregions and of classes at different scales of environmental filters such as substrate and watershed. Chironomidae are the aquatic insect of focus in this study because they are an abundant, widespread, and heterogeneous group of flies whose larvae inhabit nearly every type of aquatic habitat (Oliver, 1971; Armitage et al., 1995) and they often are numerically dominant in aquatic ecosystems, for example, comprising upwards of 50% of the abundance in streams (Coffman and Ferrington, 1996). Chironomidae may also be numerically dominant in non-stressed to pristine streams or are co- dominant with taxa typically thought to be indicative of high quality habitat such as Ephemeroptera (e.g. Pringle and Ramirez, 1998; Burgherr et al., 2002; Ruegg and Robinson, 2004). Chironomidae are particularly important to study in the Midwestern United States with over 325 species listed for the Great Plains (Hayford and Bouchard, unpublished data). Finally, chironomids show differential preferences for different substrates (Francis and Kane, 1995; Hayford and Ferrington, 2006), which make them useful in testing the robustness of stream classifications based on substrate. The objective of our study is to determine the efficacy of nutrient ecoregions in Missouri in finding natural differences in nutrient water quality concentrations and biota, specifically Chironomidae, and to search for sources of variation within these large scale classifications by also 3 looking at one very fine scale classification, substrate, and one classification, hydrologic units, that crosses nutrient ecoregional boundaries. The goals of this study are to: 1. Test the strength of nutrient ecoregion classification for Missouri with chironomid community and selected water quality parameter data. 2. Search for sources of variation within the Missouri nutrient ecoregion classes by testing the strength of a classification at a very fine scale, substrate type. 3. Test the strength of a classification using HUC designations, a classification scheme unrelated to nutrient ecoregions. 4. Test for congruence of classes using water quality and chironomid community data for the three classification schemes in an attempt to link the biota to nutrient concentrations. Methods and materials Data set Historical data on chironomid communities and nutrient water quality parameters were compiled from the same stream sites in Missouri, but under two different studies. Reference stream nutrient and chironomid data were used to test the classifications of nutrient ecoregions, hydrologic units, and substrate. The Central Plains Center for BioAssessment gathered biological assessment data from state environmental agencies in EPA Region 7 into an historical database (1984-2002) of site macroinvertebrate data from possible reference sites. Only data from one state, Missouri, and one agency, the Missouri Department of Natural Resources were used in this study to reduce variability in sampling and laboratory methodology. Specimens were collected using a 500 µm x 500 µm mesh kick

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